CN102350314B - Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent - Google Patents
Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent Download PDFInfo
- Publication number
- CN102350314B CN102350314B CN 201110273121 CN201110273121A CN102350314B CN 102350314 B CN102350314 B CN 102350314B CN 201110273121 CN201110273121 CN 201110273121 CN 201110273121 A CN201110273121 A CN 201110273121A CN 102350314 B CN102350314 B CN 102350314B
- Authority
- CN
- China
- Prior art keywords
- organic calcium
- base montmorillonite
- lignocellulosic
- calcium base
- waste water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Images
Landscapes
- Water Treatment By Sorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention relates to a lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent. The dye wastewater adsorbent is formed by compounding lignocellulose and organic calcium-based montmorillonite in a mass ratio of (1:1)-(10:1). An organic-inorganic composite material, namely the dye wastewater adsorbent which is prepared by combining the lignocellulose and the organic calcium-based montmorillonite has the characteristics of low price, environment friendliness, and no secondary pollution and the like; and raw materials have abundant sources.
Description
Technical field
The present invention relates to a kind of adsorbent, relate in particular to the compound waste water from dyestuff adsorbent of a kind of lignocellulosic and organic calcium base montmorillonite.
Background technology
Up to the present, the processing method that waste water from dyestuff is commonly used has flocculent precipitation, ozone oxidation method, photocatalytic method, membrane separation process and absorption method etc.Wherein absorption method not be owing to can introduce new pollutant, energy consumption lower and can be from waste water the concentration and separation organic pollution, thereby get more and more people's extensive concerning.
The maximum adsorbent of current use is an active carbon, because of its porous, character that specific area is big make it have the good adsorption performance.But because active carbon costs an arm and a leg, the general now composite material adsorbent that uses two or more material preparation, the weak point in the time of not only can overcoming single sorbing material and use, but also can produce some new performances.At present, composite material adsorbent has obtained in countries in the world using the most widely, and has obtained good effect.Because there are many deficiencies in traditional adsorbent, force people to study and seek cheap, environmentally safe, nontoxic, harmless new adsorbent.At present research is more comprises polyethylene/montmorillonite, level polypropylene/montmorillonoid, shitosan/imvite and shitosan/organo montmorillonite adsorbent etc.Develop nontoxic, efficient and practical adsorbent preparation method, not only can reduce production costs, of far-reaching significance to protecting human ecological environment and making full use of existing resource simultaneously.
Summary of the invention
For solving the problems of the technologies described above, the object of the present invention is to provide a kind of novel waste water from dyestuff adsorbent, this adsorbent is by adopting lignocellulosic and the compound of organic calcium base montmorillonite to obtain, have cheap, preparation technology is simple, the advantage that environmental pollution is little, security performance is high is a kind of nontoxic, efficient, new dye waste water adsorbent of using.
The present invention also aims to provide above-mentioned waste water from dyestuff preparation of adsorbent method.
For achieving the above object, the present invention at first provides a kind of waste water from dyestuff adsorbent, and it is composited by lignocellulosic and organic calcium base montmorillonite, and wherein, the mass ratio of lignocellulosic and calcium-base montmorillonite is 1: 1 to 10: 1, is preferably 6: 1.
According to concrete technical scheme of the present invention, above-mentioned waste water from dyestuff adsorbent can preferably have the lignocellulosic intercalation and enter between the lamella of described organic calcium base montmorillonite by the preparation of solution intercalation method.
According to concrete technical scheme of the present invention, preferably, the granularity of above-mentioned waste water from dyestuff adsorbent is below 200 orders, promptly can pass through 200 purpose mesh screens.
The present invention also provides above-mentioned waste water from dyestuff preparation of adsorbent method, and it is to adopt the solution intercalation method to prepare waste water from dyestuff adsorbent of the present invention, and this preparation method can may further comprise the steps:
Lignocellulosic is mixed with sodium hydroxide solution and stir, obtain lignocellulosic suspension;
The organic calcium base montmorillonite is mixed with water (being preferably distilled water) and stir, obtain organic calcium base montmorillonite suspension;
Lignin suspension is mixed with organic calcium base montmorillonite suspension, and heating makes its reaction;
To neutral, oven dry is ground and is obtained lignocellulosic and organic calcium base montmorillonite composite, i.e. waste water from dyestuff adsorbent with the product washing.
In above-mentioned preparation method provided by the invention, preferably, the concentration of sodium hydroxide solution is 5-20wt%, more preferably 10wt%.
In above-mentioned preparation method provided by the invention, preferably, the ratio of the quality of lignocellulosic and the volume of sodium hydroxide solution may be controlled to 1: 10-1: 50 (being preferably 1: 30), unit is respectively g and mL.
In above-mentioned preparation method provided by the invention, preferably, the ratio of the quality of organic calcium base montmorillonite and the volume of water may be controlled to 1: 10-1: 50 (being preferably 1: 30), unit is respectively g and mL.
In above-mentioned preparation method provided by the invention, preferably, the temperature of heating may be controlled to 20-80 ℃, and the time may be controlled to 2-10h, and more preferably, the temperature of heating may be controlled to 50 ℃, and the time may be controlled to 6h.
Above-mentioned preparation method provided by the invention can also comprise the step of preparation organic calcium base montmorillonite, preferably, the step of preparation organic calcium base montmorillonite comprises: 1.00-3.00g (being preferably 2.73g) CTAB is dissolved in 50-100mL (the being preferably 82mL) water, stirring obtains the CTAB aqueous solution, add 3.00-7.00g (being preferably 5.00g) calcium-base montmorillonite, carry out suction filtration after stirring 2-12h, profit is washed with distilled water to the AgNO of 0.01-0.5mol/L
3Till solution detected when not having precipitation, oven dry (preferred 105 ℃) was ground and is obtained the organic calcium base montmorillonite.
The present invention also provides the application of above-mentioned waste water from dyestuff adsorbent in waste water from dyestuff absorption.
Waste water from dyestuff adsorbent provided by the present invention is with lignocellulosic and the organic calcium base montmorillonite organic-inorganic nanocomposite in conjunction with preparation, have inexpensive, the source is abundant, the environmentally friendly characteristics that do not cause secondary pollution.And waste water from dyestuff adsorbent provided by the present invention is better than independent lignocellulosic and organic calcium base montmorillonite for the absorption property of dyestuff.Waste water from dyestuff adsorbent provided by the present invention can be prepared by the solution intercalation composite algorithm, and technology is simple, can energy efficient, and equipment needed thereby is also fairly simple.In addition; the preparation of the dye sorbent that lignocellulosic provided by the present invention/organic calcium based montmorillonite nanometer is compound is to making full use of the imvite resource of China's abundant; the protection environment has great importance, and has opened up new approach for the higher value application of imvite resource simultaneously.
Description of drawings
Fig. 1 is different waste water from dyestuff adsorbent to the relation curve of the mass ratio of the adsorbance of the Congo red dyestuff in the waste water and lignocellulosic and organic calcium base montmorillonite;
Fig. 2 is the different waste water from dyestuff adsorbent relation curve to adsorbance with the heating reaction temperature of the Congo red dyestuff in the waste water;
Fig. 3 is that different waste water from dyestuff adsorbent is to the adsorbance of the Congo red dyestuff in the waste water and the relation curve in heating reaction time;
Fig. 4 is the different waste water from dyestuff adsorbent relation curve to the adsorbance and the NaOH solution concentration of the Congo red dyestuff in the waste water;
Fig. 5 is the FTIR spectrogram of calcium-base montmorillonite, organic calcium base montmorillonite, lignocellulosic and lignocellulosic/organic calcium base montmorillonite composite;
Fig. 6 is the FTIR spectrogram of organic calcium base montmorillonite, lignocellulosic and lignocellulosic/organic calcium base montmorillonite composite;
Fig. 7 a is the stereoscan photograph of calcium-base montmorillonite;
Fig. 7 b is lignocellulosic/organic calcium base montmorillonite composite.
The specific embodiment
Understand for technical characterictic of the present invention, purpose and beneficial effect being had more clearly, existing technical scheme of the present invention is carried out following detailed description, but but can not be interpreted as qualification practical range of the present invention.
Present embodiment provides one group of waste water from dyestuff adsorbent, and it prepares by following steps:
With 1.00g, 2.00g, 4.00g, 6.00g, 8.00g and 10.00g lignocellulosic is that the sodium hydroxide solution of 10wt% mixes and carries out magnetic agitation with 30mL, 60mL, 120mL, 180mL, 240mL, 300mL concentration respectively, obtains six parts of different lignocellulosic suspension;
1.00g organic calcium base montmorillonite is mixed with 30mL distilled water and carry out magnetic agitation, obtain organic calcium base montmorillonite suspension;
Six parts of lignin suspension are mixed (in mixed solution with a organic calcium base montmorillonite suspension respectively, the mass ratio of lignocellulosic and organic calcium base montmorillonite was respectively 1: 1,2: 1,4: 1,6: 1,8: 1,10: 1), be heated to 50 ℃ of reaction 6h;
Utilize distilled water that the product washing is extremely neutral, 105 ℃ of oven dry are ground and are obtained six parts of lignocellulosics and organic calcium base montmorillonite composite, i.e. six parts of waste water from dyestuff adsorbents.
Six parts of waste water from dyestuff adsorbents are put into different Congo red waste water from dyestuff respectively carry out the adsorption capacity test, wherein, the concentration of Congo red dyestuff is 800mg/L in the Congo red waste water from dyestuff, and the pH value is 9.5, and adsorption time is 360min, and adsorption temp is 30 ℃.Fig. 1 is different waste water from dyestuff adsorbent to the relation curve of the mass ratio of the adsorbance of the Congo red dyestuff in the waste water and lignocellulosic and organic calcium base montmorillonite.
Present embodiment provides one group of waste water from dyestuff adsorbent, and it prepares by following steps:
With the 6.00g lignocellulosic is that the sodium hydroxide solution of 10wt% mixes and carries out magnetic agitation with 180mL concentration respectively, obtains lignocellulosic suspension;
1.00g organic calcium base montmorillonite is mixed with 30mL distilled water and carry out magnetic agitation, obtain organic calcium base montmorillonite suspension;
Five parts of lignin suspension are mixed (in mixed solution, the mass ratio of lignocellulosic and organic calcium base montmorillonite is 6: 1) respectively with a organic calcium base montmorillonite suspension, be heated to 20 ℃, 35 ℃, 50 ℃, 65 ℃, 80 ℃ reaction 6h respectively;
Utilize distilled water that the product washing is extremely neutral, 105 ℃ of oven dry are ground and are obtained five parts of lignocellulosics and organic calcium base montmorillonite composite, i.e. five parts of waste water from dyestuff adsorbents.
Five parts of waste water from dyestuff adsorbents are put into different Congo red waste water from dyestuff respectively carry out the adsorption capacity test, wherein, the concentration of Congo red dyestuff is 800mg/L in the Congo red waste water from dyestuff, and the pH value is 9.5, and adsorption time is 360min, and adsorption temp is 30 ℃.Fig. 2 is the different waste water from dyestuff adsorbent relation curve to adsorbance with the heating reaction temperature of the Congo red dyestuff in the waste water.
Present embodiment provides one group of waste water from dyestuff adsorbent, and it prepares by following steps:
With the 6.00g lignocellulosic is that the sodium hydroxide solution of 10wt% mixes and carries out magnetic agitation with 180mL concentration respectively, obtains lignocellulosic suspension;
1.00g organic calcium base montmorillonite is mixed with 30mL distilled water and carry out magnetic agitation, obtain organic calcium base montmorillonite suspension;
Five parts of lignin suspension are mixed (in mixed solution, the mass ratio of lignocellulosic and organic calcium base montmorillonite is 6: 1) respectively with a organic calcium base montmorillonite suspension, be heated to 50 ℃ and react 2h, 4h, 6h, 8h, 10h respectively;
Utilize distilled water that the product washing is extremely neutral, 105 ℃ of oven dry are ground and are obtained five parts of lignocellulosics and organic calcium base montmorillonite composite, i.e. five parts of waste water from dyestuff adsorbents.
Five parts of waste water from dyestuff adsorbents are put into different Congo red waste water from dyestuff respectively carry out the adsorption capacity test, wherein, the concentration of Congo red dyestuff is 800mg/L in the Congo red waste water from dyestuff, and the pH value is 9.5, and adsorption time is 360min, and adsorption temp is 30 ℃.Fig. 3 is that different waste water from dyestuff adsorbent is to the adsorbance of the Congo red dyestuff in the waste water and the relation curve in heating reaction time.
Present embodiment provides one group of waste water from dyestuff adsorbent, and it prepares by following steps:
With the 6.00g lignocellulosic is that the sodium hydroxide solution of 5wt%, 10wt%, 15wt%, 20wt% mixes and carries out magnetic agitation with 180mL concentration respectively, obtains four parts of different lignocellulosic suspension;
1.00g organic calcium base montmorillonite is mixed with 30mL distilled water and carry out magnetic agitation, obtain organic calcium base montmorillonite suspension;
Four parts of lignin suspension are mixed (in mixed solution, the mass ratio of lignocellulosic and organic calcium base montmorillonite is 6: 1) respectively with a organic calcium base montmorillonite suspension, be heated to 50 ℃ of reaction 6h;
Utilize distilled water that the product washing is extremely neutral, 105 ℃ of oven dry are ground and are obtained four parts of lignocellulosics and organic calcium base montmorillonite composite, i.e. four parts of waste water from dyestuff adsorbents.
Four parts of waste water from dyestuff adsorbents are put into different Congo red waste water from dyestuff respectively carry out the adsorption capacity test, wherein, the concentration of Congo red dyestuff is 800mg/L in the Congo red waste water from dyestuff, and the pH value is 9.5, and adsorption time is 360min, and adsorption temp is 30 ℃.Fig. 4 is the different waste water from dyestuff adsorbent relation curve to the adsorbance and the NaOH solution concentration of the Congo red dyestuff in the waste water.
Present embodiment provides a kind of waste water from dyestuff adsorbent, and it prepares by following steps:
With the 6.00g lignocellulosic is that the sodium hydroxide solution of 10wt% mixes and carries out magnetic agitation with 180mL concentration respectively, obtains lignocellulosic suspension;
1.00g organic calcium base montmorillonite is mixed with 30mL distilled water and carry out magnetic agitation, obtain organic calcium base montmorillonite suspension;
Lignin suspension is mixed with a organic calcium base montmorillonite suspension respectively, be heated to 50 ℃ of reaction 6h;
Utilize distilled water that the product washing is extremely neutral, 105 ℃ of oven dry are ground and are obtained lignocellulosic/organic calcium base montmorillonite composite, i.e. waste water from dyestuff adsorbent.
Lignocellulosic/organic calcium base montmorillonite composite, calcium-base montmorillonite, organic calcium base montmorillonite and lignocellulosic to the present embodiment preparation characterize.Fig. 5 is the FTIR spectrogram, and wherein, on behalf of calcium-base montmorillonite, b, a represent organic calcium base montmorillonite, c to represent the lignocellulosic that lignocellulosic, d represent present embodiment to be provided/organic calcium base montmorillonite composite.Fig. 6 is the X-ray diffraction spectrogram, and wherein, on behalf of organic calcium base montmorillonite, b, a represent the lignocellulosic that lignocellulosic, c represent present embodiment to be provided/organic calcium base montmorillonite composite.
(1) infrared spectrum (FTIR) is analyzed
According to Fig. 5 as can be seen, at 1333cm
-1Following fingerprint region calcium-base montmorillonite occurred at 911cm in the organic calcium base montmorillonite
-1The place the Al-O-H stretching vibration and at 797cm
-1, 1030cm
-1The Si-O-Si antisymmetric stretching vibration at place is again at 721cm
-1Near occurred-(CH
2) n (n 〉=4) rocking vibration absworption peak and at 1470cm
-1The place occurs-CH
3The antisymmetry deformation vibration and-CH
2The deformation vibration absworption peak, this shows that quaternary ammonium salt cationic has entered in the organic calcium base montmorillonite wafer layer.Simultaneously, the organic calcium base montmorillonite is at 2920cm
-1And 2850cm
-1The place occurs-CH
3,-CH
2Symmetry and antisymmetric stretching vibration are the absworption peak of quaternary ammonium salt organic group, and this shows that also quaternary ammonium salt has entered into the interlayer structure of organic calcium base montmorillonite.And at 1640cm
-1, 3420cm
-1And 3610cm
-1Near H-O-H stretching vibration and H-O-H flexural vibrations absworption peak have appearred respectively, this is the performance of the crystallization water in the chip layer adsorbed water of calcium-base montmorillonite and organic calcium base montmorillonite and the lattice.
Compare with the FTIR spectrogram of organic calcium base montmorillonite, in lignocellulosic/organic calcium base montmorillonite composite, the organic calcium base montmorillonite is at 797cm
-1, 911cm
-1The Mg-O-H stretching vibration at place and Al-O-H stretching vibration peak disappear, and lignocellulosic occurred at 1163cm
-1The symmetry of place-C-O-C-group and antisymmetric stretching vibration characteristic absorption peak and at 1437cm
-1Place-CH
2The in-plane bending vibration absworption peak, simultaneously, at 3416cm
-1The lignocellulosic that the place occurs-OH stretching vibration absworption peak weakens and to high wave number (3422cm
-1) move, and at 3697cm
-1, 3616cm
-1The place-OH stretching vibration absworption peak broadens and to lower wave number (3694cm
-1, 3615cm
-1) move.This shows, both existed the skeleton structure of organic calcium base montmorillonite in lignocellulosic provided by the present invention/organic calcium base montmorillonite composite, there is the big molecule of lignocellulosic to exist again, lignocellulosic-C-O-C-,-in group such as OH and the calcium-base montmorillonite molecule-coordination or complexing taken place by the interlayer cation of calcium-base montmorillonite, formed lignocellulosic/organic calcium base montmorillonite composite in OH, Si-O, Al-O key etc.
(2) X-ray diffraction (XRD) is analyzed
As seen from Figure 6, the organic calcium base montmorillonite locates to occur the obvious characteristics diffraction maximum the angle of diffraction 2 θ=4.43 °, by the Bragg equation: 2d sin θ=n λ (n=1,2,3 ...) the interlamellar spacing d=19.92nm of organic calcium base montmorillonite as can be known, and the interlamellar spacing of calcium-base montmorillonite original soil only is 1.49nm, this shows that alkyl ammonium cation with the metal cation of calcium-base montmorillonite interlayer exchange has taken place, and the CTAB cation has been inserted into the calcium-base montmorillonite interlayer.With organic calcium base montmorillonite and lignocellulosic compound after, the characteristic peak of organic calcium base montmorillonite obviously reduces and moves to low angle, the interlamellar spacing of organic calcium base montmorillonite increases to 22.29nm, show that the big molecule of the bigger lignocellulosic of volume has entered organic calcium base montmorillonite interlayer, the interlamellar spacing of organic calcium base montmorillonite is further increased, this shows, in the present embodiment, lignocellulosic and organic calcium base montmorillonite have formed the lignocellulosic/organic calcium based montmorillonite nanometer composite material with good intercal type structure, i.e. waste water from dyestuff adsorbent.
(3) ESEM (SEM) is analyzed
Fig. 7 a and Fig. 7 b are respectively the stereoscan photographs of calcium-base montmorillonite and lignocellulosic/organic calcium base montmorillonite composite.By Fig. 7 a and Fig. 7 b as can be seen, calcium-base montmorillonite surperficial dense, be the tight entity of reuniting, have an even surface and unfold, have crystal characteristic, and the lignocellulosic molecule inserts the sheet interlayer of organic calcium-base montmorillonite by the crystal structure that changes the organic calcium base montmorillonite, makes nano composite material form a loose relatively surface, illustrate between lignocellulosic and the organic calcium base montmorillonite reaction has taken place, this characterization result with FTIR and XRD is consistent.
Above characterization result illustrates that all lignocellulosic/organic calcium base montmorillonite composite (being the waste water from dyestuff adsorbent) that present embodiment provides has the structure that the lignocellulosic intercalation enters organic calcium base montmorillonite interlayer.
Table 1 is 800mg/L for the concentration of Congo red dyestuff in the Congo red waste water from dyestuff, and the pH value is 9.5, and adsorption time is 360min, and when adsorption temp was 30 ℃, different adsorbents were to the adsorption capacity correction data of Congo red dyestuff.
Table 1
| Adsorbent | Adsorbance (mg/g) |
| Lignocellulosic | 13.02 |
| Calcium-base montmorillonite | 26.49 |
| Lignocellulosic/calcium-base montmorillonite composite | 52.14 |
| Lignocellulosic/organic calcium base montmorillonite composite | 80.02 |
By the data in the table 1 as can be known, the present invention by solution intercalation composite algorithm preparation lignocellulosic and the absorption property of the compound waste water from dyestuff adsorbent (lignocellulosic/organic calcium base montmorillonite composite) of organic calcium base montmorillonite be better than lignocellulosic, the composite of calcium-base montmorillonite and lignocellulosic and calcium-base montmorillonite, and with respect to the adsorbance of lignocellulosic to Congo red dyestuff, the adsorbance of dye sorbent provided by the invention improves a lot, this explanation is with respect to its component material, and dye sorbent provided by the invention has good absorption property for Congo red dyestuff.
Above-described specific embodiment; purpose of the present invention, technical scheme and beneficial effect are further described; institute is understood that; the above only is specific embodiments of the invention; and be not intended to limit the scope of the invention; within the spirit and principles in the present invention all, any modification of being made, be equal to replacement, improvement etc., all should be included within protection scope of the present invention.
Claims (7)
1. waste water from dyestuff adsorbent, it is composited by lignocellulosic and organic calcium base montmorillonite, described lignocellulosic intercalation enters between the lamella of described organic calcium base montmorillonite, and wherein, the mass ratio of described lignocellulosic and organic calcium base montmorillonite is 1:1 to 10:1;
And described waste water from dyestuff adsorbent prepares by following steps:
Lignocellulosic is mixed with sodium hydroxide solution and stir, obtain lignocellulosic suspension, the concentration of described sodium hydroxide solution is 5-20wt%, and the ratio of the quality of described lignocellulosic and the volume of described sodium hydroxide solution is 1:10-1:50, and unit is respectively g and mL;
The organic calcium base montmorillonite is mixed with water and stir, obtain organic calcium base montmorillonite suspension, the ratio of the quality of described organic calcium base montmorillonite and the volume of water is 1:10-1:50, and unit is respectively g and mL;
Lignin suspension is mixed with organic calcium base montmorillonite suspension, and heating makes its reaction, and the temperature of described heating is 20-80 ℃, and the time is 2-10h;
To neutral, oven dry is ground and is obtained lignocellulosic and organic calcium base montmorillonite composite, promptly described waste water from dyestuff adsorbent with the product washing;
Wherein, described organic calcium base montmorillonite prepares by following steps:
The 1.00-3.00g CTAB is dissolved in the 50-100mL water, stirring obtains the CTAB aqueous solution, add the 3.00-7.00g calcium-base montmorillonite, carry out suction filtration behind the stirring 2-12h, profit is washed with distilled water to the AgNO of 0.01-0.5mol/L
3Till solution detected when not having precipitation, oven dry was ground and is obtained described organic calcium base montmorillonite.
2. waste water from dyestuff adsorbent according to claim 1, wherein, the granularity of this waste water from dyestuff adsorbent is below 200 orders.
3. waste water from dyestuff adsorbent according to claim 1, wherein, the mass ratio of described lignocellulosic and organic calcium base montmorillonite is 6:1.
4. each described waste water from dyestuff preparation of adsorbent method of claim 1-3, it may further comprise the steps:
Lignocellulosic is mixed with sodium hydroxide solution and stir, obtain lignocellulosic suspension, the concentration of described sodium hydroxide solution is 5-20wt%, and the ratio of the quality of described lignocellulosic and the volume of described sodium hydroxide solution is 1:10-1:50, and unit is respectively g and mL;
The organic calcium base montmorillonite is mixed with water and stir, obtain organic calcium base montmorillonite suspension, the ratio of the quality of described organic calcium base montmorillonite and the volume of water is 1:10-1:50, and unit is respectively g and mL;
Lignin suspension is mixed with organic calcium base montmorillonite suspension, and heating makes its reaction, and the temperature of described heating is 20-80 ℃, and the time is 2-10h;
To neutral, oven dry is ground and is obtained lignocellulosic and organic calcium base montmorillonite composite, promptly described waste water from dyestuff adsorbent with the product washing;
Wherein, described organic calcium base montmorillonite prepares by following steps:
The 1.00-3.00g CTAB is dissolved in the 50-100mL water, stirring obtains the CTAB aqueous solution, add the 3.00-7.00g calcium-base montmorillonite, carry out suction filtration behind the stirring 2-12h, profit is washed with distilled water to the AgNO of 0.01-0.5mol/L
3Till solution detected when not having precipitation, oven dry was ground and is obtained described organic calcium base montmorillonite.
5. preparation method according to claim 4, wherein, the concentration of described sodium hydroxide solution is 10wt%.
6. preparation method according to claim 4, wherein, the temperature of described heating is 50 ℃, the time is 6h.
7. the application of each described waste water from dyestuff adsorbent of claim 1-3 in waste water from dyestuff absorption.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201110273121 CN102350314B (en) | 2011-09-15 | 2011-09-15 | Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201110273121 CN102350314B (en) | 2011-09-15 | 2011-09-15 | Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN102350314A CN102350314A (en) | 2012-02-15 |
| CN102350314B true CN102350314B (en) | 2013-07-31 |
Family
ID=45574022
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN 201110273121 Active CN102350314B (en) | 2011-09-15 | 2011-09-15 | Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN102350314B (en) |
Families Citing this family (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102690487A (en) * | 2012-05-31 | 2012-09-26 | 新疆大学 | Structure-controllable cellulose graft copolymer and montmorillonite composite and preparation method thereof |
| CN103923351B (en) * | 2014-04-25 | 2016-04-27 | 安徽理工大学 | A kind of lignocellulose/the preparation method of polynite rubber reinforcing filler and the reinforcement of rubber |
| CN105107471B (en) * | 2015-09-14 | 2017-12-29 | 内蒙古农业大学 | Sulfydryl lignocellulosic/montmorillonite Composite heavy metal absorbent and preparation and application |
| CN105399963B (en) * | 2015-12-17 | 2019-04-02 | 广西大学 | A kind of mechanical activation method for preparing solid phase of lignocellulosic ester group oxidation catalyst |
| CN106215883B (en) * | 2016-09-14 | 2019-06-07 | 内蒙古农业大学 | A kind of heavy metal wastewater thereby adsorbent material and preparation method thereof |
| CN106582550A (en) * | 2016-11-10 | 2017-04-26 | 广西大学 | Lignin xanthate bentonite composite ball and preparation method thereof |
| CN106745593A (en) * | 2016-12-09 | 2017-05-31 | 吉首大学 | A kind of method of waste water in nano hydrogel material purified treatment gallic acid production |
| CN107649100B (en) * | 2017-11-09 | 2020-06-02 | 长江师范学院 | Method for preparing water treatment material by using lignin |
| CN107987290B (en) * | 2017-11-23 | 2020-07-17 | 内蒙古农业大学 | Nano lignocellulose/montmorillonite composite material and preparation and application thereof |
| CN110624510B (en) * | 2019-09-11 | 2021-10-29 | 合肥学院 | Composite adsorbent and method for treating chrome black-containing T printing and dyeing wastewater by using same |
| CN113200578B (en) * | 2021-04-15 | 2022-10-14 | 内蒙古农业大学 | Method for removing lake pollutants in cold and arid regions by utilizing natural cold energy |
| CN116144556B (en) * | 2023-03-23 | 2024-07-05 | 内蒙古农业大学 | Bacillus for treating monosodium glutamate wastewater, treating agent, and preparation method and application thereof |
| CN117264285B (en) * | 2023-09-20 | 2024-05-28 | 内蒙古农业大学 | Ethyl cellulose/montmorillonite composite material and application thereof in improving kinematic viscosity of shinyleaf yellowhorn oil |
-
2011
- 2011-09-15 CN CN 201110273121 patent/CN102350314B/en active Active
Non-Patent Citations (6)
| Title |
|---|
| P化工矿物与加工》.2009,(第5期),第4-7页. * |
| 崔继文等.十六烷基三甲基溴化铵直接处理钙基蒙脱土.《吉林大学学报(理学版)》.2007,第45卷(第2期),第297-300页. * |
| 木质纤维素-蒙脱土纳米复合材料的制备;王丽等;《功能高分子学报》;20100331;第23卷(第1期);第103-108页 * |
| 杨性坤等.有机改性蒙脱土的制备及其吸附性能研究.《IM& * |
| 杨性坤等.有机改性蒙脱土的制备及其吸附性能研究.《IM&P化工矿物与加工》.2009,(第5期),第4-7页. |
| 王丽等.木质纤维素-蒙脱土纳米复合材料的制备.《功能高分子学报》.2010,第23卷(第1期),第103-108页. |
Also Published As
| Publication number | Publication date |
|---|---|
| CN102350314A (en) | 2012-02-15 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102350314B (en) | Lignocellulose and organic calcium-based montmorillonite compounded dye wastewater adsorbent | |
| Jia et al. | Adsorption removal and reuse of phosphate from wastewater using a novel adsorbent of lanthanum-modified platanus biochar | |
| Lu et al. | Selective and superior capture of phosphate by using bimetallic bismuth-based metal-organic frameworks | |
| Zhu et al. | Highly efficient and selective removal of Cr (VI) by covalent organic frameworks: Structure, performance and mechanism | |
| CN105617981B (en) | The application in the treatment of waste water of the method for modifying of a kind of meerschaum and modified meerschaum | |
| Chen et al. | Biomass-derived composite aerogels with novel structure for removal/recovery of uranium from simulated radioactive wastewater | |
| CN102416312A (en) | Dye wastewater absorbent prepared by compounding lignocellulose and calcium-based montmorillonite | |
| Ren et al. | Comparison of Cd2+ adsorption onto amphoteric, amphoteric-cationic and amphoteric-anionic modified magnetic bentonites | |
| CN102580694B (en) | Method for preparing modified loess with high adsorption performance | |
| CN102247799B (en) | Method for removing humic acid in water by utilizing surfactant modified attapulgite | |
| Chen et al. | Functional wastepaper-montmorillonite composite aerogel for Cd 2+ adsorption | |
| CN109289772A (en) | A kind of carbon nanotube/hydrotalcite material and preparation method removing nitrate nitrogen in water removal | |
| CN103691400A (en) | Functionalized ionic liquid hybrid mesoporous molecular sieve MCM-48 composite material and preparation method and application thereof | |
| Şenol et al. | Preparation and characterization of a novel diatomite-based composite and investigation of its adsorption properties for uranyl ions | |
| Liu et al. | Preparation of AC/Cu-BTC composite and its adsorption mechanisms | |
| CN102167347B (en) | Preparation method of gemini surfactant modified montmorillonite by microwave radiation | |
| Zhang et al. | Highly efficient extraction of uranium from seawater by polyamide and amidoxime co-functionalized MXene | |
| CN106215883B (en) | A kind of heavy metal wastewater thereby adsorbent material and preparation method thereof | |
| CN110394154B (en) | Preparation method and application of moso bamboo charcoal/FeMn-LDH composite material | |
| Zhu et al. | Adsorption performance and mechanism of MoS2/BC composite for U (VI) from aqueous solution | |
| CN106955677A (en) | It is a kind of based on ion liquid modified egg shell/acticarbon and preparation method thereof | |
| Liu et al. | Uranium uptake with graphene oxide sponge prepared by facile EDTA‐assisted hydrothermal process | |
| Beig et al. | Adsorption of Cr (VI) by NaOH-modified microporous activated carbons derived from the wastes of Amaranthus retroflexus, Magnolia soulangeana, and Tanacetum Vulgar L.: mechanism, isotherms, and kinetic studies | |
| Wu et al. | Eco-friendly biomass aerogels from moxibustion waste for sustainable remediation of organic contaminants | |
| Tewatia et al. | Highly fluorescent composite of boron nitride quantum dots decorated on cellulose nanofibers for detection and removal of Hg (II) ions from waste water |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant |